Table of Contents Table of Contents
Previous Page  17 / 48 Next Page
Information
Show Menu
Previous Page 17 / 48 Next Page
Page Background

mercury deposition

from precipitation

volcanic eruptions

release mercury

natural volatilization

and runoff from rocks

and minerals

dry deposition of

particulate mercury

mercury

volatilization and

runoff from gold

and mercury mines

mercury

mines

n

a

t

u

r

a

l

industrial

discharge

into

aquatic

systems

burning of

fossil fuels

releases mercury

coal electric plant

factory

crop burning and

forest fires release

mercury to

atmosphere

mercury pathway

to humans is

fish consumption

mercury

bioaccumulation

in fish

mercury in water and

sediment reaches fish

sediments

mercury evaporation

from lakes and rivers

mercury

evaporation

from oceans

domestic

sewage

mercury

vapor

possible seepage

in ground water

landfill

mercury

vapor

Mines use toxic chemicals

including cyanide, mercury, and

sulphuric acid, to separate metal from ore. The chemicals used

in the processing are generally recycled, however residues may

remain in the tailings, which in developing countries are often

dumped directly into lakes or rivers with devastating conse-

quences. The accidental spillage of processing chemicals can

also have a serious impact on the environment. For example, at

The Acid Mine Drainage (AMD)

is the number one environmental problem facing the

mining industry. AMD occurs when sulphide-bearing minerals in rock are exposed

to air and water, changing the sulphide to sulphuric acid. It can devastate aquatic

habitats, is difficult to treat with existing technology, and once started, can continue

for centuries (Roman mine sites in Great Britain continue to generate acid drainage

2 000 years after mining ceased). Acid mine drainage can develop at several points

throughout the mining process: in underground workings, open pit mine faces, waste

rock dumps, tailings deposits, and ore stockpiles. (Miningwatch).

Artisanal small-scale gold mining of placer deposits

occurs mostly in developing

countries. Examples include Brazil, Venezuela, Colombia, Guyana, Suriname, Philip-

pines and New Guinea. Between 10 and 15 million people worldwide produce 500

to 800 tonnes of gold per year, in the process emitting as much as 800-1000 tonnes

of mercury. Gold recovery is performed by removing sediments from the river and

adjacent areas and feeding them through a number of mercury-coated sieves. The

mercury amalgamates with the gold in the sediments, separating the gold from the

rest of the material. The gold-mercury amalgam is then heated. The heat drives off

the mercury, leaving the gold product. While most of the mercury condenses and is

recovered, some is emitted to the air and is eventually deposited on nearby land or

water surfaces. Mercury deposited on land ultimately reaches streams and rivers

through runoff. Roughly 1 kilogram of mercury enters the environment for every kilo-

gram of gold produced by artisans. (United States Geological Survey).

the Baia Mare mine in Romania cyanide is used to extract gold

from slurry. In January 2000 a dam containing tens of thou-

sands of tonnes of slurry burst, poisoning the local river with

cyanide and heavy metals. Up to 100 tonnes of cyanide were

released into the river, a tributary of the Danube. The drink-

ing water supply for more than 2 million people was affected.

Within hours, dead fish were seen washed up along the river.

16

17

After Mining

Filtering soils

Groundwater

Surface runoff

Mine

Sulfide

OXYGEN + WATER + SULPHIDE = SULFURIC ACID

Heavy Metals Fish Mortality

Filtering soils

Groundwater

Rainfall filtering

through soil

Surface runoff

Before Mining

Sulfide

Extraction decreases groundwater depth and

natural filtration, and increases the

groundwater contamination.